US9308496B2 - System and method for controlling and reducing NOx emissions - Google Patents
System and method for controlling and reducing NOx emissions Download PDFInfo
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- US9308496B2 US9308496B2 US12/766,584 US76658410A US9308496B2 US 9308496 B2 US9308496 B2 US 9308496B2 US 76658410 A US76658410 A US 76658410A US 9308496 B2 US9308496 B2 US 9308496B2
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- 239000000446 fuel Substances 0.000 claims description 15
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 claims description 12
- 238000002485 combustion reaction Methods 0.000 claims description 9
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Images
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/74—General processes for purification of waste gases; Apparatus or devices specially adapted therefor
- B01D53/86—Catalytic processes
- B01D53/8621—Removing nitrogen compounds
- B01D53/8625—Nitrogen oxides
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/74—General processes for purification of waste gases; Apparatus or devices specially adapted therefor
- B01D53/75—Multi-step processes
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2251/00—Reactants
- B01D2251/40—Alkaline earth metal or magnesium compounds
- B01D2251/404—Alkaline earth metal or magnesium compounds of calcium
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2251/00—Reactants
- B01D2251/60—Inorganic bases or salts
- B01D2251/606—Carbonates
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2252/00—Absorbents, i.e. solvents and liquid materials for gas absorption
- B01D2252/10—Inorganic absorbents
- B01D2252/103—Water
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2255/00—Catalysts
- B01D2255/10—Noble metals or compounds thereof
- B01D2255/102—Platinum group metals
- B01D2255/1021—Platinum
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2257/00—Components to be removed
- B01D2257/40—Nitrogen compounds
- B01D2257/404—Nitrogen oxides other than dinitrogen oxide
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2257/00—Components to be removed
- B01D2257/50—Carbon oxides
- B01D2257/502—Carbon monoxide
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/14—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by absorption
- B01D53/1431—Pretreatment by other processes
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/92—Chemical or biological purification of waste gases of engine exhaust gases
- B01D53/94—Chemical or biological purification of waste gases of engine exhaust gases by catalytic processes
- B01D53/9404—Removing only nitrogen compounds
- B01D53/9409—Nitrogen oxides
Definitions
- This invention is generally in the field of NO x emission abatement. More particularly, the present invention is directed to systems and methods for reducing NO x emissions from NO x producing sources.
- NO x emissions are a concern for many industries, particularly in power-generating industries. NO x production is common in high-temperature combustion applications and/or with the combustion of nitrogen-bearing fuels. At high combustion temperatures, diatomic nitrogen in the combustion air may be oxidized to produce NO x . Nitrogen in the fuel may also be released as free radicals during combustion to form NO x . NO x emissions are generally known to cause acid rain as well as deleterious health side effects and are, therefore, a subject of regulatory scrutiny.
- a method for reducing NO x emissions from a gas stream produced by a production source may comprise oxidizing a substantial portion of NO gas present in the gas stream by contacting the gas stream with an oxidation catalyst to yield higher order N x O y molecules; and thereafter removing higher order N x O y molecules from the gas stream by solvent absorption or reaction.
- a system for reducing NOx emissions.
- the system may comprise a gas production source configured to produce a gas stream comprising NO x ; an oxidation catalyst positioned downstream of the gas production source, wherein the oxidation catalyst is configured to oxidize NO gas molecules in the gas stream to yield higher order N x O y molecules; and a removal device positioned downstream of the oxidation catalyst configured to remove higher order N x O y molecules from the gas stream by solvent absorption or reaction.
- FIG. 1 is a diagram, illustrating a system for reducing NO x emissions in accordance with one or more embodiments of the present invention.
- Systems and methods are provided for reducing NO x emissions from NO x producing sources.
- the systems and methods may be used in various NO x producing applications, including, but not limited to, gas combustion, steam production, and hydrocarbon refining applications.
- the systems and methods may generally be employed in any application in which a gas stream comprising NO x is produced.
- systems and methods of the present invention may be employed to reduce NO x emissions from a gas turbine engine.
- systems and methods of the present invention may be employed to reduce NO x emissions from a boiler.
- systems and methods of the present invention may be employed to reduce NO x emissions from a refinery.
- Systems and methods of the present invention may achieve abatement of NO x from a gas stream primarily by the oxidation of NO molecules in the gas stream to higher order N x O y molecules, and the subsequent removal of the higher order N x O y molecules by solvent absorption or reaction.
- Such an approach may advantageously avoid or reduce the need for the continuous injection of reducing agents.
- the system may remove 80 to 95% of NO x from the post-combustion gas stream without the addition of reactants to the gas stream.
- such an system may reduce or eliminate the need for addition of oxidizing agents or energy sources such as ozone (O 3 ) to create N x O y species with higher solvent absorption or reaction like N 2 O 5 .
- higher order N x O y molecules refers to N x O y molecules in which the value of x and/or y is greater than 1. These molecules may be the product of the oxidation of NO.
- higher order N x O y molecules encompasses NO 2 and N 2 O 5 .
- the term also encompasses other nitrogen oxides that are of a higher order than NO, including N 2 O, N 2 O 3 , and N 2 O 4 .
- methods for reducing NO x emissions from a gas stream produced by a production source.
- the method may comprise oxidizing a substantial portion of NO gas present in the gas stream by contacting the gas stream with an oxidation catalyst to yield higher order N x O y molecules (such as NO 2 and/or N 2 O 5 ), and thereafter removing NO 2 gas from the gas stream by aqueous absorption or reaction.
- the term “oxidation catalyst” generally refers to a device that oxidizes NO molecules to yield higher order N x O y molecules, e.g., NO 2 and/or N 2 O 5 .
- the oxidation catalyst may be a flow through device having an internal honeycomb structure coated with the chemical catalyst.
- the oxidation catalyst may be a CO catalyst.
- the oxidation catalyst is configured to oxidize a sufficient quantity of NO molecules in the gas stream such that the majority of N x O y molecules in the gas stream exiting the oxidation catalyst are NO 2 molecules.
- the majority of NO x molecules in the gas stream are NO molecules before the gas stream is contacted with the oxidation catalyst.
- the oxidation catalyst may be placed at a location along the gas stream flow path where it will be exposed to gas stream temperatures in the range of about 350° F. to about 700° F. It has been found that operating the oxidation catalyst at such a temperature range may advantageously allow the catalyst to thermodynamically favor the production N x O y due to the lower operating temperature while providing an adequate temperature to achieve the desired rate kinetics over the catalyst surface. It has also been found that the presence of SO x to the exhaust stream may shift the optimal temperature to the higher value.
- a conventional gas turbine engine may produce a gas stream in which about 90% of the NO x molecules are NO.
- the oxidation catalyst may be configured to produce a gas stream in which about 50% or more of the NO x molecules are higher order N x O y molecules (e.g., NO 2 , and or N 2 O 5 ), or more preferably about 70% or more of the NO x molecules are higher order N x O y molecules, or even more preferably about 80% or more of the NO x molecules are higher order N x O y molecules.
- N x O y molecules e.g., NO 2 , and or N 2 O 5
- greater than 80% higher order N x O y in NO x may be achieved at temperatures of about 700° F. or below.
- An oxidation efficiency of about 85% may be achieved in the range of about 350° F. to about 700° F. using a platinum-based oxidation catalyst. The range may vary depending on catalyst composition, catalyst surface treatment, and catalyst surface area.
- the method may further comprise combusting a fuel to produce the gas stream, wherein the gas stream comprises the reaction products of the combustion of the fuel.
- the fuel may comprise a hydrocarbon fuels, a non-hydrocarbon fuel or combinations thereof.
- the fuel may comprise natural gas, oil or coal.
- the gas stream may be produced by various production sources including, but not limited to, a gas turbine, a boiler, a furnace, refinery, or a chemical processing plant.
- Higher order N x O y molecules in the gas stream may be removed downstream of the oxidation catalyst by solvent absorption (such as by aqueous absorption) or reaction.
- the higher order N x O y molecules are soluble in water, and may be removed from the gas stream by applying water to the gas stream. For example, water may be sprayed into the gas stream to absorb higher order N x O y molecules in the gas stream.
- the water and higher order N x O y molecules may be thereafter separated from the gas stream.
- a water collector adapted to condense water vapor in the gas stream may be placed downstream of the oxidation catalyst.
- an aqueous or other solvent film is support on a high surface area structure, such as a demister pad, and N x O y transport to the film.
- the condensed water may absorb higher order N x O y molecules in the gas stream and the water and higher order N x O y molecules may be thereafter separated from the gas stream.
- the higher order N x O y molecules may be separated by reaction of the higher order N x O y molecules with a reactant. For example, NO 2 molecules may contact and react with soda lime, such as in a lime based water solution.
- the oxidation of NO molecules to higher order N x O y molecules and aqueous absorption and/or reaction of the higher order N x O y molecules is performed in a manner effective to remove at least 40% of the NO x molecules from the gas stream.
- the oxidation of NO molecules to higher order N x O y molecules and aqueous absorption and/or reaction of the higher order N x O y molecules is performed in a manner effective to remove at least 75% of the NO x molecules from the gas stream.
- Such a level of NO x reduction may advantageously be achieved without the addition of ammonia.
- the system may comprise a gas production source configured to produce a gas stream comprising NO x ; an oxidation catalyst positioned downstream of the gas production source, the oxidation catalyst configured to oxidize NO gas molecules in the gas stream to yield higher order N x O y molecules; and a removal device positioned downstream of the oxidation catalyst configured to remove N x O y molecules from the gas stream by aqueous absorption or reaction.
- the system may include a gas production source that is configured to combust a fuel to produce the gas stream comprising the reaction products of the combustion of the fuel.
- the fuel may comprise a hydrocarbon fuel such as natural gas, oil or coal.
- the gas stream may be produced by various production sources including, but not limited to, a gas turbine, a boiler, a furnace or a chemical processing plant (such as a refinery).
- Higher order N x O y molecules in the gas stream may be removed downstream of the oxidation catalyst by aqueous absorption or reaction.
- the higher order N x O y molecules are soluble in water, and may be removed from the gas stream by applying water to the gas stream.
- water may be sprayed into the gas stream by a water injecting device, e.g., through one or more spray nozzles, to absorb higher order N x O y molecules in the gas stream.
- the water and higher order N x O y molecules may be thereafter separated from the gas stream.
- a water collector adapted to condense water vapor in the gas stream may be placed downstream of the oxidation catalyst.
- the condensed water may absorb higher order N x O y molecules in the gas stream and the water and higher order N x O y molecules may be thereafter separated from the gas stream.
- the higher order N x O y molecules may be separated by reaction of the higher order N x O y molecules with a reactant.
- the higher order N x O y molecules may contact and react with soda lime solution.
- the oxidation of NO molecules to higher order N x O y molecules and aqueous absorption and/or reaction of the higher order N x O y molecules is performed in a manner effective to remove at least 40% of the NO x molecules from the gas stream.
- the oxidation of NO molecules to higher order N x O y molecules and aqueous absorption and/or reaction of the higher order N x O y molecules is performed in a manner effective to remove at least 75% of the NO x molecules from the gas stream.
- Such a level of NO x reduction may advantageously be achieved without the addition of ammonia.
- FIG. 1 An embodiment of a system for reducing NOx emissions is illustrated in FIG. 1 .
- the system 10 may have a NO x production source, such as a gas turbine engine 12 .
- the gas turbine engine 12 may produce a gas stream having an exhaust temperature of about 800 to about 1200° F. and a NO x concentration of 9 ppm. Approximately 10% of the NO x emissions may comprise NO 2 and the balance primarily NO.
- the gas stream may pass through one or more heat exchangers 14 so that the gas stream may be cooled to about 350 to about 800° F.
- the gas stream may then pass through an oxidation catalyst 16 where a substantial portion of the NO molecules are oxidized to higher order N x O y molecules.
- a NO x production source such as a gas turbine engine 12 .
- the gas turbine engine 12 may produce a gas stream having an exhaust temperature of about 800 to about 1200° F. and a NO x concentration of 9 ppm. Approximately 10% of the NO x emissions may comprise NO 2 and
- the gas stream exiting the oxidation catalyst 16 may have a NO x concentration of 9 ppm with approximately 80% of the NO x emissions comprising NO 2 or other higher order nitrogen oxides such as N 2 O 5 .
- the gas stream may then be further cooled to about 120° F. in a heat exchanger 18 .
- the cooled gas stream may then pass through a vessel 20 where the N x O y is scrubbed in a solvent, such as an aqueous solvent, and absorbed or reacted and then removed from the gas stream.
- the vessel 20 may comprise a water injecting device that injects water or other solvent for N x O y into the gas stream.
- the vessel 20 may comprise a water collecting device that condenses water vapor in the gas stream. The liquid water and absorbed higher order N x O y molecules may then be separated from the gas stream and the gas stream may then pass through the exhaust 22 to the atmosphere.
- the exhaust gas stream may comprise 2.5 ppmvd NO x .
- the vessel 20 may comprise soda lime or another reactant for NO 2 .
- Aqueous absorption and/or reaction of higher order N x O y molecules may be achieved in various ways. For example, for fuels with high sulfur content, aqueous absorption and/or reaction of higher order N x O y molecules may be performed as part of a flue gas desulfurization (“FGD”) process within an FGD unit.
- FGD flue gas desulfurization
- Various types of scrubbers may be employed to separate the higher order N x O y molecules from the gas stream including spray towers, packed bed scrubbers, and/or venturi scrubbers.
- a system for reducing NO x emissions comprising a gas production source configured to produce a gas stream comprising NO x and an oxidation catalyst positioned downstream of the gas production source.
- the oxidation catalyst may be configured to oxidize NO gas molecules in the gas stream to yield higher order N x O y molecules.
- the system may further comprise a removal system positioned downstream of the oxidation catalyst configured to remove higher order N x O y molecules from the gas stream by aqueous absorption or reaction.
- the majority of NO x molecules present in the gas stream are NO molecules before the gas stream contacts the oxidation catalyst.
- approximately 90% of the NO x molecules in the turbine exhaust may be NO.
- the oxidation catalyst may oxidize about 50% or more of the NO molecules produced by the production source. In certain embodiments, the oxidation catalyst may oxidize about 75% or more of the NO molecules produced by the production source.
Abstract
Description
Claims (7)
Priority Applications (4)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
US12/766,584 US9308496B2 (en) | 2010-04-23 | 2010-04-23 | System and method for controlling and reducing NOx emissions |
JP2011089659A JP2011230120A (en) | 2010-04-23 | 2011-04-14 | SYSTEM AND METHOD FOR CONTROLLING AND REDUCING NOx EMISSION |
EP11163244A EP2380654A1 (en) | 2010-04-23 | 2011-04-20 | System and Method for Controlling and Reducing NOx Emissions |
CN2011101127383A CN102233238A (en) | 2010-04-23 | 2011-04-21 | System and method for controlling and reducing NOx emissions |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
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US12/766,584 US9308496B2 (en) | 2010-04-23 | 2010-04-23 | System and method for controlling and reducing NOx emissions |
Publications (2)
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US20110262334A1 US20110262334A1 (en) | 2011-10-27 |
US9308496B2 true US9308496B2 (en) | 2016-04-12 |
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US12/766,584 Active 2031-05-18 US9308496B2 (en) | 2010-04-23 | 2010-04-23 | System and method for controlling and reducing NOx emissions |
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US (1) | US9308496B2 (en) |
EP (1) | EP2380654A1 (en) |
JP (1) | JP2011230120A (en) |
CN (1) | CN102233238A (en) |
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US8437941B2 (en) | 2009-05-08 | 2013-05-07 | Gas Turbine Efficiency Sweden Ab | Automated tuning of gas turbine combustion systems |
US9671797B2 (en) | 2009-05-08 | 2017-06-06 | Gas Turbine Efficiency Sweden Ab | Optimization of gas turbine combustion systems low load performance on simple cycle and heat recovery steam generator applications |
US9267443B2 (en) | 2009-05-08 | 2016-02-23 | Gas Turbine Efficiency Sweden Ab | Automated tuning of gas turbine combustion systems |
US9354618B2 (en) | 2009-05-08 | 2016-05-31 | Gas Turbine Efficiency Sweden Ab | Automated tuning of multiple fuel gas turbine combustion systems |
US7914747B1 (en) * | 2010-04-23 | 2011-03-29 | General Electric Company | System and method for controlling and reducing NOx emissions |
JP2014005964A (en) * | 2012-06-22 | 2014-01-16 | Miura Co Ltd | NOx TREATMENT SYSTEM OF BOILER |
EP2685066A1 (en) * | 2012-07-13 | 2014-01-15 | Alstom Technology Ltd | Gas turbine power plant with flue gas recirculation and catalytic converter |
JP5765376B2 (en) | 2012-08-30 | 2015-08-19 | 株式会社豊田中央研究所 | Exhaust gas purification device for internal combustion engine |
US9381462B2 (en) * | 2013-07-01 | 2016-07-05 | General Electric Company | System and method for reducing emissions via solvent injection |
JP6672996B2 (en) * | 2016-04-28 | 2020-03-25 | 富士電機株式会社 | Source analysis apparatus and source analysis method |
JP6702547B2 (en) * | 2016-07-28 | 2020-06-03 | 株式会社東芝 | Denitration system and denitration method |
CN106377978B (en) * | 2016-11-07 | 2022-07-12 | 天津海泰环保科技发展股份有限公司 | Comprehensive treatment system for rubber waste gas |
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JP2011230120A (en) | 2011-11-17 |
US20110262334A1 (en) | 2011-10-27 |
EP2380654A1 (en) | 2011-10-26 |
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